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EC number: 259-715-3 | CAS number: 55589-62-3
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1995-Jul-18 through 1995-Dec-12
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
- Report date:
- 1995
Materials and methods
- Objective of study:
- toxicokinetics
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: German testing guidelines of December 1989; European community note for guidance of February 1983 (Council Recommandation 831571)
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 6-methyl-1,2,3-oxathiazine-4(3-H)-one-2,2-dioxide potassium salt
- IUPAC Name:
- 6-methyl-1,2,3-oxathiazine-4(3-H)-one-2,2-dioxide potassium salt
- Reference substance name:
- 6-methyl-1,2,3-oxathiazin-4(3H)-one 2,2-dioxide, potassium salt
- EC Number:
- 259-715-3
- EC Name:
- 6-methyl-1,2,3-oxathiazin-4(3H)-one 2,2-dioxide, potassium salt
- Cas Number:
- 55589-62-3
- Molecular formula:
- C4H5NO4S.K
- IUPAC Name:
- potassium 6-methyl-2,2,4-trioxo-3,4-dihydro-1,2λ⁶,3-oxathiazin-3-ide
- Reference substance name:
- Acesulfame potassium
- IUPAC Name:
- Acesulfame potassium
- Test material form:
- solid: crystalline
- Details on test material:
- - Name of test material (as cited in study report): Acesulfame K (SunettTM)
- Substance type: sweetener
- Physical state: cyrstalline powder
- Analytical purity: 99.8%
- Impurities (identity and concentrations): fluoride <1 µg/g, arsenic <0.01 µg/g, seleniu < 0.1 µg/g, leasd <0.05 µg/g
- Lot/batch No.: D 01 NAAG 50
- Expiration date of the lot/batch: 1998-Dec-31
- Stability under test conditions: stable
Constituent 1
Constituent 2
Constituent 3
- Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Hoechst AG, Kastengrund, Germany
- Age at study initiation: young adult
- Weight at study initiation: males: mean 146.9 - 148.7 g, females: mean 109.3 - 116.6 g
- Fasting period before study: not applicable
- Housing:
- Individual metabolism cages: yes/no
- Diet: libitum (Altromin 1321 powder (Altromin GmbH, Lage, Germany)
- Water: ad libitum (tap water)
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 23 °C
- Humidity (%): 55 ± 15 %
- Air changes (per hr): regularly
- Photoperiod (hrs dark / hrs light): 12 h/12h
IN-LIFE DATES:
From: 1995-Jul 18
To: 1995-Aug-02
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- other: diet
- Details on exposure:
- DIET PREPARATION
- Rate of preparation of diet (frequency): once for the study duration (2 weeks)
- Mixing appropriate amounts with (Type of food): The final dietary mixtures were prepared by using 1 kg premix, adding the necessary amount of Altromin and mixing for 30 min in a precision mixer to produce the required concentrations (9 000 and 15 000 ppm
- Storage temperature of food: room temperature
HOMOGENEITY AND STABILITY OF TEST MATERIAL:
Was analytically verified - Duration and frequency of treatment / exposure:
- 2 weeks, continuous administration via the diet
Doses / concentrations
- Remarks:
- Doses / Concentrations:
9000 (males: 855 g, females: 827 g), 15000 ppm (males: 1367 g, females: 1277 g)
- No. of animals per sex per dose / concentration:
- 48
- Control animals:
- no
- Positive control reference chemical:
- Not applicable
- Details on study design:
- - Dose selection rationale: based low subchronic toxicityy
- Rationale for animal assignment (if not random): not applicable (random) - Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled (delete / add / specify): serum
- Time and frequency of sampling: during the last 24 h prior to termination at 30 min intervals in each 1 male and 1 female - Statistics:
- Not applicable
Results and discussion
- Preliminary studies:
- Not applicable
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Not applicable
- Details on distribution in tissues:
- Not applicable
- Details on excretion:
- Not applicable
Toxicokinetic parametersopen allclose all
- Test no.:
- #1
- Toxicokinetic parameters:
- AUC: 9000 ppm: males; 848.2 µg.h/ml, females:933.5 µg.h/ml; 15000 ppm: males 1520.6 µg.h/ml, females: 1671.1 µg.h/ml
- Test no.:
- #2
- Toxicokinetic parameters:
- Cmax: 9000 ppm: males: 55.2 µg/ml, females: 71.0 µg/ml; 15000 ppm: males: 108.0 µg/ml, females: 119.3 µg/ml
- Test no.:
- #3
- Toxicokinetic parameters:
- other: C (average) 9000 ppm: males: 35.32 µg/ml, females: 38.9 µg/ml; 15000 ppm: males: 63.4 µg/ml, females: 69.6 µg/ml
Metabolite characterisation studies
- Metabolites identified:
- not measured
- Details on metabolites:
- Not applicable
Bioaccessibility (or Bioavailability)
- Bioaccessibility (or Bioavailability) testing results:
- Not applicable
Any other information on results incl. tables
Pharmacokinetic profile:
The level of Acesulfame potasium ranged from 16.1 to 71.0 µg/ml in the 9000 ppm group and from 30.3 to 119.3 µg/ml in the 15000 ppm group. Maximum concentrations were mainly observed during dark hours (18:00 to 6:00), whereas all minimum concentrations were determined during light hours (6:00 to 18:00). This indicates that food intake was predominantely over night.
9000 and 15000 ppm Levels in serum (µg/ml) |
|
|
|
|
Time of the day |
9000 ppm |
9000 ppm |
15000 ppm |
15000 ppm |
01.08. 09:00 |
31.2 |
41.4 |
108.0 |
56.5 |
01.08. 09:30 |
24.0 |
36.0 |
54.1 |
80.3 |
01.08. 10:00 |
28.0 |
35.1 |
58.7 |
83.2 |
01.08. 10:30 |
31.9 |
42.1 |
64.8 |
68.6 |
01.08. 11:00 |
32.3 |
24.9 |
74.7 |
94.9 |
01.08. 11:30 |
17.1 |
29.7 |
55.6 |
79.6 |
01.08. 12:00 |
23.8 |
32.8 |
53.0 |
71.8 |
01.08. 12:30 |
35.3 |
31.0 |
76.8 |
53.4 |
01.08. 13:00 |
21.7 |
39.6 |
48.9 |
84.8 |
01.08. 13:30 |
26.2 |
24.0 |
53.6 |
38.1 |
01.08. 14:00 |
32.3 |
22.1 |
39.4 |
39.7 |
01.08. 14:30 |
21.7 |
21.7 |
40.5 |
36.9 |
01.08. 15:00 |
35.0 |
52.4 |
31.8 |
49.8 |
01.08. 15:30 |
22.8 |
25.7 |
40.1 |
40.7 |
01.08. 16:00 |
24.5 |
16.2 |
43.6 |
38.0 |
01.08. 16:30 |
22.2 |
16.1 |
42.2 |
46.2 |
01.08. 17:00 |
19.3 |
53.7 |
34.3 |
50.8 |
01.08. 17:30 |
31.6 |
20.4 |
43.2 |
30.3 |
01.08. 18:00 |
35.7 |
28.9 |
50.2 |
55.9 |
01.08. 1 8:30 |
38.6 |
19.4 |
30.4 |
36.7 |
01.08. 19:00 |
26.0 |
54.9 |
91.2 |
48.3 |
01.08. 19:30 |
28.9 |
24.6 |
55.1 |
83.7 |
01.08. 20:00 |
36.9 |
18.6 |
58.2 |
46.7 |
01.08. 20:30 |
32.8 |
24.2 |
36.0 |
89.6 |
01.08. 21:00 |
38.5 |
37.0 |
71.4 |
69.7 |
01.08. 21:30 |
35.7 |
39.5 |
59.7 |
52.8 |
01.08. 22:00 |
45.4 |
38.6 |
77.4 |
119.3 |
01.08. 22:30 |
42.6 |
50.5 |
56.3 |
83.3 |
01 .08. 23:00 |
32.6 |
47.4 |
63.6 |
80.0 |
01.08. 23:30 |
50.7 |
45.7 |
61.3 |
60.9 |
02.08. 00:00 |
54.5 |
41.8 |
71.8 |
106.7 |
02.08. 00:30 |
50.0 |
62.6 |
75.6 |
82.4 |
02.08. 01:00 |
55.2 |
63.3 |
80.5 |
44.1 |
02.08. 01:30 |
46.0 |
42.9 |
82.3 |
95.1 |
02.08. 02:00 |
41.8 |
40.2 |
84.5 |
107.8 |
02.08. 02:30 |
35.0 |
71.0 |
97.0 |
104.1 |
02.08. 03:00 |
31.7 |
56.5 |
74.3 |
93.6 |
02_08. 03:30 |
51.9 |
33.1 |
66.5 |
93.9 |
02.08. 04:00 |
40.3 |
31.1 |
68.6 |
76.1 |
02.08. 04:30 |
38.8 |
59.3 |
99.0 |
69.9 |
02.08. 05:00 |
54.6 |
53.1 |
82.1 |
75.9 |
02.08. 05:30 |
44.4 |
51.4 |
69.2 |
79.3 |
02.08. 06:00 |
45.5 |
50.1 |
61.7 |
88.1 |
02.08. 06:30 |
48.0 |
63.3 |
79.6 |
88.8 |
02.08. 07:00 |
33.7 |
31.3 |
55.9 |
73.0 |
02.08. 07:30 |
31.0 |
44.9 |
74.9 |
56.6 |
02.08. 08:00 |
43.3 |
44.7 |
74.4 |
59.7 |
02.08. 08:30 |
25.2 |
31.9 |
68.7 |
76.4 |
Dose dependency
The increase of AUC(24h) was virtually proportional to the dose level. The 1.7 fold increase in dose was followed by an 1.8 fofd increase in AUC.
Pharmacokinetic parameters in the serum:
9000 ppm
|
Male |
Female |
C(max, µg/ml) |
55.2 |
71.0 |
T(max) |
01:00 |
02:30 |
C(min, µg/ml) |
17.1 |
16.1 |
T(min) |
11:30 |
16:30 |
C(av, µg/ml) |
35.3 |
38.9 |
AUC(0-24, µg.h/ml) |
848.2 |
933.5 |
15000 ppm
|
Male |
Female |
C(max, µg/ml) |
108.0 |
119.3 |
T(max) |
09:00 |
22:00 |
C(min, µg/ml) |
30.4 |
30.3 |
T(min) |
18:30 |
17:30 |
C(av, µg/ml) |
63.4 |
69.6 |
AUC(0-24, µg.h/ml) |
1520.6 |
1671.1 |
Sex differences
Remarkable sex differences have not been observed. The levels and consequently also the AUC in female rats were about 10 % higher than in male rats
Feed consumption
The mean feed consumption in the second week was in group 1 (9000 ppm) 20.4 and 13.6 g per day in male and female rats, respectively. In group 2 (15000 ppm), 19.9 and 13.0 g were consumed per day in male and female rats, respectively.That corresponds to doses of 854 and 827 mg/kg bw/d (9000 ppm) and to doses of 1367 and 1277 mg/kg bw/d (15000 ppm) in male and female rats, respectively.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): bioaccumulation potential cannot be judged based on study results
At days 14/15, the AUC(0-24) after feeding of 9 000 ppm was 848.2 µg.h/ml in male and 933.5 µg.h/ml in female rats. At 15000 ppm the AUC(0-24) was 1520.6 µg.h/ml in male and 1671.1 µg.h/ml in female rats. - Executive summary:
Acesulfame potassium was administered to groups of 48 male and 48 female Wistar rats for 2 weeks mixed in the feed at a concentration of 9000 ppm and 15 000 ppm. During the last 24 hours of the study serum samples were taken from 1 male / 1 female animal per group at 30 minutes intervals. Acesulfame K was measured in serum.
This study is assessed as appropriate and valid since it was performed according to internationally accepted testing guidelines under GLP conditions and reporting, assessment and data presentation in the study report was considered as appropriate.
At days 14/15, the AUC(0-24) after feeding of 9000 ppm was 848.2 µg.h/ml in male and 933.5 µg.h/ml in female rats. At 15000 ppm the AUC(0 -24) was 1520.6 µg.h/ml in male and 1671.1 µg.h/ml in female rats. The pharmacokinetic parameter AUC (24h) increased proportional to the given dose in the investigated range from 9000 to 15000 ppm. No remarkable sex differences were observed.
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